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Canada Urges
Removal of Mold Hazard from Homes
By Steve Sauer
A simplistic residential guideline proposed by the Canadian
government in December situates household mold as a potential health
hazard. In a plainly worded draft guideline, the country’s health
agency recommends that citizens “clean thoroughly any mould growing
in residential buildings ... regardless of the mould species found
to be growing in the building.”
Health Canada also stresses in the residential guideline that
citizens can prevent mold growth when they “control humidity and
diligently repair any water damage in residences.”
The proposed Health Canada guideline cites scientific animal studies
and literature reviews over the past five years that associate
indoor dampness with asthma and lung inflammation. The guideline
also holds that cell walls of molds contain a certain compound with
inflammatory properties, and that mold spores and mycelial fragments
contain allergens.
Dr. J. David Miller, a scientific consultant to Health Canada’s Air
Health Effects Division, contributed to the drafting of a larger and
more detailed document that has been used in Canadian courts. Health
Canada’s new guideline is a summary of this document, said Miller,
who is a biochemistry professor at Carleton University in Ottawa and
also a member of the Biosafety and Environmental Microbiology
Committee of the American Industrial Hygiene Association.
With Thomas G. Rand and two researcher from St. Mary’s University in
Halifax, Miller and a fellow researcher at Carleton University
coauthored one of two papers published in 2005, cited by the Health
Canada Guideline, that observed lung inflammation and asthma-like
responses in rodents exposed to a common indoor mold or its toxins.
Their study, which deals with Penicillium chrysogenum, was
published in the journal Toxicological Sciences.
The other referenced study took place not in Canada but in the
United States. In that study, University of North Carolina-Chapel
Hill environmental scientist Yong-joo Chung and others found
“dose-dependent allergic asthma-like responses in mice” from
exposure to the same species of mold.
One of that study’s coauthors, Dr. Stephen Vesper, works with the
National Exposure Research Laboratory in Cincinnati, under the U.S.
Environmental Protection Agency. “The fact is that every indoor
environment contains mold,” Vesper told IE Connections.
“However, not every mold is found in indoor environments and
certainly not at the same concentration in each home. Therefore, it
has been our goal to try to understand the difference between a
water-damaged home and non-water-damaged home. To this end, we have
published many studies describing the development of the Relative
Moldiness Index.”
Three such papers containing Vesper’s contributions appear in 2004
editions of Systematic and Applied Microbiology, Journal of
Environmental Monitoring, and Journal of Occupational and
Environmental Medicine. Vesper’s presentations on this topic also
included the Indoor Air Quality Association’s annual meetings in
2005 and 2006, as well as the April 2006 open house sponsored by the
Florida Inter-County IAQ Council.
Vesper also detailed how the Relative Moldiness Index has taken on a
more practical application since EPA’s collaboration with another
arm of the federal government, the U.S. Department of Housing and
Urban Development.
“We have now extended this work to the national scale, with the
recent completion, in conjunction with HUD, of the American Healthy
Home Survey,” he said. “The result has been the development of the
Environmental Relative Moldiness Index ... based on the analysis of
36 species in a representative set of nearly 1,100 U.S. homes using
a highly standardized dust sample.”
Vesper has used the Environmental Relative Moldiness Index, or ERMI,
in epidemiological studies appearing in the August 2006 editions of
Environmental Health Perspectives and the Journal of Occupational
and Environmental Medicine.
The Health Canada guideline was issued Dec. 23, and a public comment
period was announced that would last through at least Feb. 20.
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New Mailings from EEF Number in the Hundreds
Foundation Repeats Misinformation EPA Wants Stopped
By Steve Sauer
The Environmental Education
Foundation issued promotional materials in about 300 separate
mailing lists in one week last month, not only dodging federal
government demands that EEF stop spreading information deemed to be
misleading, but also assuming the names of an array of groups with
which EEF is not affiliated.
E-mails EEF sent during the
third week of January distributed messages that the U.S.
Environmental Protection Agency has upon previous occasions called
intentionally misleading. An IE Connections investigation has
identified 302 separate mailing lists that are maintained on EEF’s
Web site, nearly all of which were used between Jan. 16 and 19 to
promote an upcoming training session EEF claimed was the result of a
contract with the EPA.
The overwhelming majority of
these mailing lists assume the identities of a broad base of
organizations, companies and publications. These e-mails were sent
with the name of each mailing list appearing in the “from” field,
along with the common e-mail address sending them all –
info@enviro-ed.org, which is
the main contact e-mail address EEF lists on its Web site.
For instance, any people who
found themselves subscribed to the mailing list “kreia,” or
“Kentucky Real Estate Inspection Assoc.,” saw that name used as the
sender of the e-mail that was really from EEF. It was also true of
those who had been subscribed to regional mailing lists like
“International Facilities Management Assoc. San Fernando Valley” and
international mailing lists like “International Code Council.”
Each e-mail apologized for
“the short notice” and said EEF had “just received the approval for”
a $200 subsidized registration to attend EEF’s online two-day mold
training to be held Feb. 15–16 for a total payment reduced from $495
to $295. EEF’s mailing does not identify the source of any subsidy
authorization.
In a strikingly similar
message sent in February 2006, EEF used a $200 subsidy to promote
another training session that was to be held Feb. 15–16 of that
year.
In lists for contractors and
property managers, EEF publicized another $200 subsidy – this for
online training to take place Dec. 13–14 – announced between Nov. 30
and Dec. 6 with differing registration deadlines but with a
recurring message: “sorry for the short notice, but we just received
the approval for the $200.00 subsidy.”
Making last month’s series
of EEF announcements unique over past e-mail solicitations was the
employment of hundreds of mailing lists to deliver the foundation’s
message online to mass audiences, deceptively: Of the 302 mailing
lists discovered are several named for various entities in the IAQ
industry, including IE Connections. E-mails sent between Jan. 16 and
19 appearing to be from the American Industrial Hygiene Association,
National Air Filtration Association, Indoor Air Quality Association
and American Indoor Air Quality Council prompted the organizations
to distribute their own mailings to affected constituents between
Jan. 19 and 23.
Less than 12 hours after
IAQA members reported receiving an e-mail promoting EEF training
from a mailing list called “iaqa” on Jan. 19, the association sent
an official e-mail to its entire membership explaining that the
earlier e-mail was not authorized by IAQA. In its alert to members,
IAQA spoke for itself and a handful of other affected entities in
the IAQ industry, saying that they “are not affiliated with EEF, nor
do they endorse or approve the EEF training programs described in
the recent EEF emails.”
The IAQ Council, NAFA and
AIHA delivered similar messages over the next four days.
AIHA responded first by contacting EEF directly, said AIHA’s
executive director, Steven Davis. “We went to EEF and politely
demanded that they cease and desist from using our name or acronym
in any way shape or form,” Davis told IE Connections on Jan. 22. He
said his assistant at AIHA, Peter O’Neil, left a phone message
asking EEF “to inform anyone registering for their course that AIHA
was not and never has been an endorser of their program.”
Davis said he believed EEF
would comply with AIHA’s warning. “Hopefully, this will be the end
of their transgressions,” he said.
In an e-mail on Jan. 23,
AIHA informed its members of the association’s non-endorsement of
the EEF training. “We felt it was important for our members to know
that AIHA does not officially support this organization or this
program, regardless of the impression with which their marketing may
leave you,” AIHA told its members.
“It is unfortunate that
emails using deceptive tactics have been used to potentially mislead
those in the IAQ industry,” IAQA informed its members, urging them
“to exercise extreme caution and to perform careful research prior
to contracting for training and/or certification services with
organizations and individuals who employ such tactics.”
“Energy Star,” the name of
one particular mailing list info@enviro-ed.org utilized in promoting
the EEF training, is a trademark registered to the U.S.
Environmental Protection Agency dating back to September 1996. A
Jan. 19 e-mail sent to recipients on the Energy Star list contained
the same information as all the others that week, opening with the
line, “New Training As A Result Of EPA Contract.”
The same language has
appeared on the front page of EEF’s Web site since November 2005,
despite the agency’s protests in 2006 that it does not endorse or
approve of the training. Elsewhere on the Web site and in separate
marketing efforts, EEF has used the EPA’s distinctive seal in ways
suggestive of a connection.
Reacting to such marketing,
legal counsel for the EPA in October demanded EEF cease and desist
in using the agency’s logo and seal in such marketing and outreach
materials. EEF reportedly ignored a 30-day deadline to respond to
the EPA demand, and references to the EPA as a partner with EEF
continued to appear on the organization’s Web site as this issue
went to press in January.
Dr. David Mudarri, who
retired last month and is credited with founding the EPA’s Indoor
Environments Division, had disclosed to IE Connections in December
2005 that “EEF received an unsatisfactory rating” on an EPA contract
effective between March 29, 2004, and Aug. 31, 2005, “because they
failed to satisfactorily meet the performance requirements of the
contract.” The sum of EPA payments to EEF on the contract was
$43,678, and the EPA withheld more than 12 percent of the payment
for the foundation’s poorly rated performance under the contract.
Many EEF marketing
materials, including the most recent e-mails, share a declaration
attributed to Mudarri in which he announces that the contract has
been awarded. It is from the statement of work Mudarri issued to EEF
at the onset of the contract in 2004, and it does not reflect the
strained relationship between the foundation and the EPA that
emerged over time.
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WORD ON THE STREET
VOICES
“I would be very suspicious of that organization if it’s one that Al
Gore supported. If it’s one that he supported, then I probably wouldn’t
support it.”
— Edward J. Cirillo, who was a Republican state
senator in Arizona between 1996 and 2003, speaking about the
Environmental Education Foundation in a telephone interview on Jan. 19,
in response to a question of whether or not he is correctly listed,
alongside Gore, on the EEF Web site as having once sent a letter of
support to EEF; while Cirillo said he could not recall such a letter,
his support of the organization was verified when EEF provided IE
Connections an undated letter printed on state letterhead and signed by
Cirillo; Gore’s office confirmed that a quotation on EEF’s Web site that
is attributed to the former vice president is “old but accurate”
MOST OZONE GENERATORS ALWAYS ON
Most Calif. residents owning ozone-emitting air cleaners run them every
day and continuously, a survey in the state has determined. A study
released last month, believed to be the first in California to analyze
trends in the purchase and use of air cleaners, estimates that 10
percent of the state’s households are exposed to ozone emitted either
intentionally or as a byproduct and that most of these machines are
never turned off. Of California households in which the primary air
cleaner emits ozone, 65.5 do not turn off the devices off at any time in
a given week. The number for air cleaners designated as purposeful ozone
generators, rather than those for which ozone is a byproduct, is
slightly higher: 72 percent. The statewide survey of 2,019 adults was
conducted last year by the University of California Survey Research
Center in Berkeley, under contract with the California Air Resources
Board.
Proceeding to draft regulations on ozone emissions
from indoor air cleaners, the Board has scheduled a public workshop to
be held March 29 in Sacramento. Anyone unable to attend the workshop in
person may participate by telephone and Web; for more information, visit
www.arbc.ca.gov.
STL COMPLETES TESTAMERICA MERGER
The combination of Severn Trent Laboratories with TestAmerica is now
complete, STL announced Jan. 9 in a statement crediting the move with
the creation of a “new environmental testing market leader.” Severn
Trent Laboratories sold last year to TestAmerica Holdings for a reported
figure of nearly $162 million. Also according to the release, “The
combined company will have 54 analytical laboratories and dozens of
service centers and microlabs strategically located across the United
States.” The move aligns Aerotech P&K, an affiliate of STL, with EMLab,
the analytical mold testing division of TestAmerica. EMLab specializes
in the analysis of molds, yeasts, bacteria and allergens. The Aerotech
P&K team, formed by a 2004 merger, combines the capabilities of Aerotech
Laboratories Inc. with P&K Microbiology Services Inc. STL operations in
the United States included 32 laboratories, 16 service centers, and QED
Environmental Systems. “This combination is a defining moment for
TestAmerica and STL,” said TestAmerica CEO Tom Barr. “We look forward to
building on our combined strengths to provide the best possible service
to our clients, create a positive and rewarding working environment for
our employees, and realize the potential of the new company.”
TestAmerica is an affiliate of H.I.G. Capital, a private investment
firm. STL was previously operated by Severn Trent PLC, whose chief
officer said last year that it the U.S. Laboratories division was “no
longer regarded as being a core business for the future.”
MORE NEWS FROM LIBBY
While the U.S. Environmental Protection Agency defended its work in
decreasing asbestos exposure to residents of Libby, Mont., January was
also marked by a disturbing new study revealing that respiratory
disease-related deaths for most of last century were higher among those
working in mines near Libby than for the average U.S. citizen.
The more prolonged the exposure to vermiculite was
for miners translated to better chances they would contract one of
several fatal diseases, writes author Patricia A. Sullivan of the
National Institute for Occupational Safety and Health, in an article
published in Environmental Health Perspectives. In the article, Sullivan
calls for more research in the health effects experienced by various
kinds of workers when they are exposed to vermiculite insulation inside
home attics in that town. “Vermiculite from the mine near Libby,
Montana, is contaminated with tremolite asbestos and other amphibole
fibers,” she explains in the report. This could affect electricians,
plumbers, and people installing cable or repairing phone lines in homes,
increasing their risk of dying from asbestosis, lung cancer,
mesothelioma and cancer of the pleura, reports Sullivan.
EPA’s Region 8, which covers Montana and other
states, said that a December report by the agency’s acting inspector
general was misinformed and off base. The inspector general’s report
said that because the agency has not conducted a comprehensive amphibole
asbestos toxicity assessment in Libby, it was failing to follow internal
guidance. In the response, obtained by IE Connections on Jan. 29, the
EPA rebutted that a toxicity assessment was skipped because it would
have delayed cleanup, which was determined to be the more urgent need.
The EPA said that it has spent $154 million in Libby and completed 794
residential and commercial property cleanups, and that toxicity studies
would be part of the next phase of risk assessment.
Sen. Max Baucus of Montana, who in December said he
was “outraged” by revelations in the inspector general’s report, could
not be reached for comment on his reaction to the Region 8 response. A
senior member of the Senate Environment and Public Works Committee
overseeing the EPA, Baucus had previously called for a congressional
hearing into the asbestos cleanup.
TORONTO PLANS FOR COOLING SEASON
Over 30 buildings in Toronto’s financial district are being cooled by an
alternative to conventional air-conditioning. Cold water from 272 feet
below the surface of Lake Ontario is moved via pipes to a city pumping
station, kicking off a process a press release says is capable of
cooling 34.5 million square feet of office space and saving customers
millions of dollars in electric power usage, all while eliminating
ozone-depleting refrigerants and removing 79,000 tons of carbon dioxide
from the air. Steve Martile, project manager at Toronto-based Enwave
Energy Corp., said the system’s long-term success depends on
disinfecting and filtering the water so that impurities do not coat the
heat exchanger plates and so that suspended matter does not provide
nutrients for biological growth. Either problem, said Martile, would
lower the system’s efficiency, require higher disinfection treatment
costs, and possibly damage system components. A centrifugal sand
filtration system manufactured by Sonitec Inc. is designed to remove
solids that are under half a micron in size, thereby protecting the
Enwave cooling system against impurity buildup and biological growth. In
12-week tests conducted after Sonitec’s Vortisand filtration system was
installed in September 2005, total particle count in the chilled water
was reduced by 89.6 percent and total suspended solids were reduced by
96.5 percent.
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Effect of Appeals to S520 Felt
Minimally at IICRC
By Steve SauerTwo challenges to the
process of revising the mold remediation standard filed by ex-members of
the consensus body would result in few actions to be taken by the
Institute of Inspection, Cleaning and Restoration Certification,
according to responses IICRC distributed in late December and early
January.
As reflected in IICRC’s responses to appeals
alleging numerous policy violations in the standard’s revision process
over the past year, only minor actions would be taken to correct some
past wrongs. IICRC denied all of the major allegations illuminated by
former S520 drafters Elisa Larkin and Carl Grimes.
In nearly all cases, IICRC said the incidents
alleged were too old to be reviewable, citing a 15-day moratorium on
reporting offenses taking place in the process. Even in those cases,
IICRC provided sometimes lengthy responses analyzing the allegation and,
in a few cases, said corrective actions would be taken.
Responding to separate suggestions by Larkin and
Grimes that the IICRC ought to revert to older versions of the document,
IICRC refused to do so. Reverting to a previous version would be
“ineffective, detrimental or unnecessary,” the organization said in its
responses to both appellants.
Also indicated in IICRC’s responses was that
since both appeals were filed, a subsequent meeting of the S520
consensus body in Tampa performed further work on revising the standard.
In some cases, the consensus body was able to resolve issues brought
forth in both appeals, said IICRC.
Larkin, who had co-chaired the document’s
Inspection and Preliminary Determination section, cut her ties with the
S520 body on Oct. 28 and filed an appeal Nov. 29 highlighting 14
possible violations of IICRC policies.
IICRC deflected an assertion in Larkin’s appeal
that, in at least one instance, “changes were left up to those who could
remember what work had been done” at a meeting for which minutes were
“lost.” In its response, IICRC called the allegation disingenuous and
said that, in one or two instances in which a day’s worth of work was
lost due to a hardware failure, “work was simply redone” by “the entire
Editing Committee.”
According to IICRC, if any errors were made in
the process, there would still be ample time for members of the
consensus body to correct them before the S520 revision is finalized.
Whenever participants at the Dec. 7–9 meeting in
Tampa brought up incidents related to recordkeeping, IICRC told Larkin,
“in every instance an adequate explanation was provided or the
misunderstanding corrected.”
Grimes, a regular contributor to IE Connections
and a member of its Editorial Advisory Board, did not comment publicly
in November on the reasons he decided to resign from the S520 body on
Nov. 29. However, he said in his appeal, filed Dec. 5, that the
appearance of a conflict of interest was “one of several factors in my
resignation.”
“Concerns of dominance, undue influence and
hidden influence have arisen,” Grimes said in his appeal. “Claims of
fact, chronology and potential conflicts of interest were presented
behind limitations of confidentiality that precluded adequate review
and/or correction.”
In its response to Grimes, IICRC dismissed the
allegation due to a lack of specificity, saying he had failed to
demonstrate a policy violation. IICRC had dismissed notions of dominance
with specificity in its response to Larkin, saying that while two
section chairs, Jim Holland and John Banta, are both employees of
Restoration Consultants, “The Secretariat does not believe that the
employment connection ... establishes dominance on a consensus body that
contains 26 voting members.” It also said that Holland and Banta
“routinely disagree on matters of import before the Consensus Body, and
do not appear to have formed any kind of alliance or dominant
coalition.”
When Grimes was a member of the S520 body, he
chaired the section devoted to indoor environmental professionals. The
S520 body subsequently agreed during the Dec. 7–9 meeting in Tampa
resolved complaints from the Indoor Air Quality Association regarding
IICRC’s previously expressed intentions to acquire a trademark on the
term. Following the meeting, IICRC announced while the revised standard
would continue to use the term, the organization would no longer pursue
the trademark.
The timing of IICRC’s responses to both appeals
fulfilled the organization’s obligation to respond within 30 days, as
policy stipulates.
Many of the allegations had no adverse effects,
IICRC reported, and so the appellants’ proposed remedies were not
enacted. IICRC did, however, indicate it would take one action as a
result of Grimes’ appeal. It said, “To the extent some meeting minutes
may not have been ‘approved’ by the S520 Consensus Body, those minutes
will be circulated and submitted for approval.”
In an e-mail Grimes sent two days after
receiving IICRC’s response to his appeal, he indicated he was not
satisfied with his understanding of how the term “secretariat” is used
throughout the response. Grimes had stated in his appeal that he was
unclear as to whether the secretariat was an individual or an
organization, to which IICRC replied, “The IICRC is the Secretariat.”
Grimes received the IICRC response as an
attachment in an e-mail sent to him by IICRC attorney Mark Hansen.
Grimes said he believed this indicated IICRC had treated his appeal as a
“legal challenge to be defended rather than an ANSI procedural issue to
be resolved.” He said it was “troubling” to see that “the response was
directed to be forwarded through the office of the ‘IICRC General
Counsel.’”
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Maine Leads States in Lung Association’s
Report
6 States Banned Smoking Indoors in 2006, Earning High Marks
By Steve SauerThe American Lung Association’s annual “State of
Tobacco Control” report grades the U.S. federal government, the 50
states, the District of Columbia and Puerto Rico in four categories
related either directly or indirectly to health. Only one state,
Maine, holds the distinction of receiving straight A’s across the
board, as it has done so for a second year in a row.
“It’s an evolving thing, and it’s a cultural thing. It takes time
to get people’s practices to change,” Gov. John E. Baldacci of Maine
told IE Connections on Jan. 10. “The real impacts are going to be
seen tomorrow, not just in dollars in cents but in lives being
saved.”
Despite Maine’s achievements in smoke-free air and the three
other categories the Lung Association tracks in its report –
cigarette taxes, youth access, and spending on tobacco prevention
and control – Maine nonetheless ranks 15th highest among the 50
states in smoking-attributable death rate, according to the most
recent annual estimates available. Maine’s rate of 303.8
smoking-attributable deaths per 100,000 exceeds the national average
of 284.8. Nine southern states have higher rates than Maine, with
Kentucky being the highest, at 378.1. Utah claims the lowest rate
among states, at 144.9.
To protect health, the nonprofit Maine Indoor Air Quality Council
in 1999 adopted a position paper on environmental tobacco smoke.
That paper, developed in only the council’s second year of existence
and revised once since, holds that only by eliminating tobacco smoke
can the hazards be mitigated.
At the time of that statement, California was the only state to
have legislated a smoking ban indoors, and time was running out on
other states to become smoke-free by the year 2000, heeding a call
from 1985 by C. Everett Koop, surgeon general during the Reagan
administration. Other states did not pick up on the task until after
that deadline had passed, but Delaware picked up on it in 2002, and
Maine and New York followed in 2003.
Since then, as detailed in the American Lung Association’s
report, more than a dozen other states and territories have gone
smoke-free or plan to, with the tally doubling between this year and
last. Just seven states were smoke-free as 2006 began, with six more
added to the list throughout the year, and a smoking ban took effect
in the District of Columbia last month.
The trend is to continue this year as Puerto Rico is set to ban
smoking indoors next month, with Arizona following in May. Utah and
Montana have both passed bans to be implemented in 2009.
Successes of the earliest statewide smoking bans may account for
the spurt of states going smoke-free in recent months, said Paul
Billings, the American Lung Association’s vice president of policy
and advocacy. Those who anticipate smaller receipts would result
from laws prohibiting smoking in bars and restaurants turned out to
be wrong, said Billings. “The economic gloom and doom did not come
to pass,” he said in an interview on Jan. 9, the day the report was
released to the public.
The report emphasizes university studies in 2004 and 2005 that
prove smoking bans in Florida and Massachusetts, respectively, did
not decrease sales in restaurants and the other types of
establishments whose economies they analyzed.
Also referenced in the report is a 2004 study from New York
City’s Department of Finance showing an increase in business
receipts after the city’s smoking ban took effect in January 2003.
Californians had previously witnessed a similar effect, noting
increased alcohol sales in bars and restaurants during the years
immediately after that state became the first to enact a ban.
Billings said such experience shows that residents of such places
have become conditioned to expect smoke-free air wherever they go.
Lawmakers in 2006 may have also been prompted into action after
the June 27 release of a U.S. Surgeon General report on secondhand
smoke. Titled “The Health Consequences of Involuntary Exposure to
Tobacco Smoke,” the report railed against manufacturers of
air-filtration technology designed to remove cigarette smoke and
other pollutants from the air, concluding that, “Exposures of
nonsmokers to secondhand smoke cannot be controlled by air cleaning
or mechanical air exchange.” It further holds that “banning smoking
from the workplace is the only effective way to ensure that
exposures are not occurring.”
The surgeon general’s conclusions were based on a review of
literature including a 2005 statement approved by the board driving
the American Society of Heating, Refrigeration and Air-Conditioning
Engineers. That statement said that no existing technologies “have
been demonstrated or should be relied upon to control health risks
from secondhand smoke exposure in spaces where smoking occurs.”
ASHRAE’s statement also factors into the bodies of research
informing the American Lung Association’s report. Dr. Norman
Edelman, chief medical officer for the association’s New York
headquarters, told IE Connections, “The more you look, the more
scientific studies are done [that show] more deleterious effects.”
Referencing a study in Ireland that shows bartenders’ health
improved after a nationwide indoor smoking ban took effect in pubs,
Edelman said, “We have an obligation to make the workplace safe as
well as the general environment.”
Manufacturers of filtration devices admit that their technologies
are incapable of creating an invisible barrier between smoking and
non-smoking areas, as well as removing all the particulates and
contaminants present in cigarette smoke. However, air filtration can
“reduce airborne contaminants to acceptable levels,” said Duke
Wiser, president of Dynamic Air Quality Solutions, the manufacturer
of air-filtration devices used in some national restaurant chains
and country clubs.
“The use of physical separation barriers and high-efficiency
filtration devices can effectively isolate contaminants within
smoking areas,” said David M. Shagott, president of Abatement
Technologies Inc. “This is done by placing those areas under
negative pressure, and employing single-pass ventilation, i.e.,
ducting the air exhausted from the room directly to the outdoors.”
Abatement manufactures a filtration system that healthcare
facilities use to isolate infectious pathogens.
Wiser made the following theoretical argument in support of
smoking in workplaces: “If there can be Class 10 cleanrooms, then
there can be smoking areas that don’t adversely impact non-smoking
areas,” he said. “So we see the question not as ‘Can it be done?’
but, rather, ‘How much will it cost?’ and ‘Is it worth the cost?’”
In contrast, Edelman and Billings contested that the only
financial burden on owners of restaurants and bars is affording the
signs that tell customers that smoking is prohibited.
“My response is always the same,” said Edelman. “Show me the
proof. If they can do it, that’s OK. But I think that’s foolish.”
In Maine, the governor told IE Connections he believes
establishments investing in such technology are making an unwise
decision for various reasons. “It’s more expensive, and it just
doesn’t work. It costs money, and it takes time to install,” said
Baldacci.
“I tell everybody to make the leap. It’s not going to hurt them.”
Baldacci said one trend he has observed sweeping across various
industries including the food industry is making reductions toxins
and chemicals. “People are finding out in the business world, in the
food world, that it makes sense to be sensitive to these issues,” he
said.
Doing anything contrary to reducing pollutants, he said, is “just
a waste of time and money.”
Asked for his advice on how other politicians could implement
smoking bans, Baldacci answered simply. “I think the best experience
is just to put it into practice,” he said.
Baldacci said he shares the American Lung Association’s belief
that smoking bans will eventually be implemented in all states and
communities. “They might as well just go to the point where we’re
all going to be at,” he said.
The American Lung Association announced a challenge for all
indoor spaces throughout the United States to become smoke-free by
2010. While, on one hand, it places the deadline 10 years later than
Koop’s 1985 suggestion, Billings said this goal is attainable and
may be achieved well ahead of schedule. “We’ve been pleasantly
surprised at how fast we’ve seen progress in the last year, and
there’s been much talk about legislation and regulation,” he said.
Billings touted the work of Koop and his successors in the role
of surgeon general, including Vice Adm. Richard H. Carmona, whose
four years as surgeon general ended in July, one month after he
issued the secondhand smoke report. “The report was a great help,”
said Billings.
The Surgeon General’s office has been temporarily held since July
by Rear Adm. Kenneth P. Moritsugu, who previously held the office in
an interim capacity for the six months prior to Carmona’s takeover
in August 2002.
Billings said the Surgeon General’s office has a “bully pulpit” –
which he also likened to “a very big megaphone” – that can be used
“to advocate on behalf of the health of America.”
Asked what more could be regulated nationally to protecting
Americans from secondhand smoke, Edelman said, “The single best
thing the federal government can do is to raise the federal excise
tax.” That tax is currently 39 cents per pack of 20 cigarettes, and
the American Lung Association wants the federal government to hike
the tax by $2. “It’s trivial compared to where it should be,” said
Edelman.
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Air Cleaner Cases Speak to Truth in Advertising
David M. Governo, Esq.
Partner
Governo Law Firm LLC
Boston, Mass.
Sarah Governo Allar
Paralegal
Governo Law Firm LLC
Boston, Mass.
The perils of over-promising and under-delivering have become
even clearer in light of recent settlements concerning the marketing
of air purifiers from Brookstone and Sharper Image.
Brookstone sold both its own Pure-Ion model and Sharper Image’s
Ionic Breeze air purifiers. These companies implied results that the
products apparently did not deliver. Disgruntled customers filed
lawsuits claiming that the companies deceived them and that the
products did not effectively remove dust, pollen and other
impurities from the air, thus failing to perform their marketed and
warranted purpose. These lawsuits were recently settled, and the
court documents supporting the settlements tell an interesting story
about the hazards of overzealous advertising.
Brookstone
In accordance with the settlement agreement, Brookstone must mail
class notices by Feb. 12, describing the suit and the settlement to
all persons who purchased a full-room Pure-Ion air purifier other
than the Pure-Ion Advanced. Brookstone is also directed to publish
the class notices in USA Today.
Brookstone is to give each member of the settlement class a $20
store credit toward the purchase of any Brookstone product and valid
for one year. Members of the settlement class may opt to return
their units for a store credit equal to the purchase price paid.
In addition, the settlement agreement enforces multiple
conditions regarding the production of the Pure-Ion air purifier.
Prior to future marketing or mass production, units must be
submitted for testing of its clean air delivery rate, the standard
for overall efficiency and effectiveness of indoor air purifiers.
CADR indicates the volume of contaminant-free air delivered by an
air purifier, measuring smoke on a scale of 10 to 450, dust on a
scale of 10 to 400, and pollen on a scale of 25 to 250. The higher
the numbers, the faster the unit filters the air.
The only full-room ionizing air purifiers Brookstone can continue
selling under the settlement are new units that achieve an average
CADR of more than 100 in the three categories and that also meet the
Underwriters Laboratory’s Standard 867 standards for ozone
emissions.
The settlement agreement also forces Brookstone to alter its
marketing by May 1. In all marketing materials, Brookstone must
publish average CADRs and any reference to CADR testing must include
a statement providing a link to a Web site that explains CADR
testing and provides a summary of the actual test results.
Brookstone advertising, product packaging and owners’ manuals for
full-room ionizing purifiers must include a statement that the unit
is “not a medical device.” Furthermore, Brookstone is prohibited
from referring to the Pure-Ion or the Ionic Breeze as the “leading
silent air purifier” or from using language indicating that the unit
effectively cleans the air.
A hearing for the final approval of the settlement is set for
April 5. The costs of the attorneys’ fees portion of the lawsuit are
limited to $1.2 million. However, the full cost remains unknown and
depends on how many members of the settlement class return their
products and use their $20 vouchers.
Sharper Image
The Sharper Image settlement dealt with similar issues for the Ionic
Breeze air purifier. A settlement on Jan. 16 requires the company:
- to offer $19 merchandise credits to the 3.2 million
consumers who purchased the products,
- to sell Ozone Guard attachments for $7 per unit,
- to test all Ionic Breeze models for ozone emissions using
the UL 867 test protocol, and
- to restrict its advertising.
With respect to the advertising restrictions, Sharper Image
has agreed:
- to make claims based solely on reliable scientific testing,
- not to state that the Ionic Breeze is a medical device, and
- not to claim that ozone produces health benefits.
Sharper Image will pay the plaintiffs’ attorneys’ fees up to
$1.875 million.
In 2004, Sharper Image sued Consumers Union, publisher of
Consumer Reports, with claims of libel and that a negative review of
the Ionic Breeze air purifier was false and malicious. Not only was
the case dismissed, but Sharper Image was required to pay defense
costs.
An article (David Governo, “New Advice: Let the Sellers of Air
Cleaners Beware”) appearing in the October 2004 issue of IE
Connections, reports several specific investigations and rulings
from the Federal Trade Commission, which regulates claims made
against companies regarding the products that they sell. The author
also contributed to the 2006 “Best and Worst of IAQ” in the December
2006 issue, describing the worst as “ozone generation, chlorine
dioxide and other ‘cures’ [that] still have limited applications but
apparently endless marketing opportunities.”
The recent settlement and accompanying documents show that the
marketing opportunities of ozone-generating air purifiers now do
have their limits.
These settlements serve as a warning to other manufactures of air
purifiers that may be at risk for litigation due to claims they
make. Since false or deceptive advertising can cost a company
millions of dollars, it is imperative for companies to analyze their
potential for liability and to use careful, precise and accurate
language in advertising.
David M. Governo is a partner with Governo Law Firm LLC. Sarah
Governo Allar, his daughter, is working as a paralegal at the firm
until she begins an international relations internship in Argentina.
The firm helps clients in preventing and resolving legal problems
including business, environmental and IAQ claims. The firm also
advocates for individuals and companies in local and national
litigation, and counsels them in business planning, including risk
management and regulatory compliance. David Governo can be reached
by e-mail at
dgoverno@governo.com or by phone at (617) 737-9047.
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Encapsulating Fungal Growth, Leaving It in Place
Dr. Harriet Burge
Director of Aerobiology
Environmental Microbiology Laboratory Inc.
San Bruno, Calif.
Encapsulants are commonly used to prevent exposure to lead and to
asbestos. Encapsulants are designed to bond with the surface to be
encapsulated and essentially glue the objectionable material
permanently in place. Encapsulation with respect to the fungi means
adding some kind of coating or otherwise ensuring that spores will
not be released. It is, of course, possible to do this, and
encapsulation may be the method of choice in some cases.The only
time that I have agreed to encapsulate fungal growth was in a very
large warehouse where the exposed fireproofing had become moldy. The
water source was a one-time event that was very unlikely to
re-occur. While abundant spores remained, the fungi were no longer
actively growing. Removing the fireproofing would have been
unreasonably expensive (including lost work time). The encapsulant
was sprayed on; then, every surface in the warehouse was either
vacuumed or wiped clean with a damp cloth. Air sampling one week
following encapsulating showed very few fungal spores in the air. In
the years since this was done, there have been no re-occurrence of
growth and no exposure complaints.
The key points in the decision to use encapsulating in this case
were:
- The water problem was solved (in this case, a one-time
event).
- The fungi were no longer actively growing (meaning that the
material was dry).
- Normal healthy adults occupied the space.
- Removing the moldy material would have been unreasonably
expensive to the extent that the space would probably have to be
abandoned.
These four points must be addressed in each case where
encapsulation is considered. First, whatever water problem occurred
that led to fungal growth must have been corrected before
encapsulation occurs, and must be such that the same event is
unlikely to occur again. Fungi will grow on encapsulating materials,
and there is no point in adding encapsulants to the fungal food mix
if water is going to again become available.
Before encapsulating any fungi, the substrate must be completely
dry. Encapsulating damp material will probably allow the fungi to
continue growing right through the encapsulant.
I don’t generally recommend using encapsulants in hospitals or
similar places where immunocompromised people live. On the other
hand, the method may be completely safe in such situations if done
properly, and could avoid the considerable cost associated with
other forms of remediation. More study will be needed before we can
be sure that this method is reasonable in these cases.
Finally, using an encapsulant should be considerably less
expensive than actually removing all of the moldy material. Getting
rid of all of the fungal material is always best, when possible.
Remember: If you have fixed the water problem and removed all of the
mold growth, then encapsulants should not be necessary.
An interesting article on encapsulating ventilation system ducts
can be found in the April 2004 ASHRAE Journal. This article supports
the idea that prevention of the water problem is the best approach
to preventing fungal growth. Two of the encapsulating methods did
work, but so did removal of the fibrous (water-absorbing) liner from
the ducts.
What kinds of encapsulants can be used? Ideally, one would use
something that will not support fungal growth and that doesn’t
contain water. The decision on what specific encapsulant to use is
up to the investigator with consideration of the location, extent,
likelihood of abrasion, any minute possibility of the return of
water, cost, etc. There are encapsulants specifically designed for
encapsulating mold. These contain biocides designed to prevent mold
growth on the encapsulant. I don’t generally like to use biocides
but rather recommend fixing the water problem.
The Web site of Michigan’s Department of Community Health lists
state-approved encapsulants for use on lead-containing surfaces. (Go
to www.michigan.gov/mdch
and click on “Physical Health & Prevention,” then “Prevention” and
then “Lead Poisoning.” Under the “Lead Professionals” category,
click on “List of Approved Encapsulants.”) It is possible that these
would also be useful for encapsulating fungal growth. Asbestos
encapsulation often involves using several coats of encapsulant: the
first to glue the fibers together and the second to fill in the
spaces. This may be the method of choice for fungi as well.
Dr. Harriet Burge is director of aerobiology at Environmental
Microbiology Laboratory Inc. and associate professor and director of
the microbiology laboratory at the Harvard School of Public Health.
Widely considered the leading expert in IAQ, Burge pioneered the
field more than 30 years ago. She has served as a member of three
National Academy of Sciences committees for IAQ, including as vice
chair of the Committee on the Health Effects of Indoor Allergens.
To submit a question to Dr. Burge, write to her by e-mail at
askdrburge@emlab.com. All
questions posed to Burge will receive a reply, although space
limitations prevent us from publishing them all. By submitting a
question, you agree to have your question and its answer published
in a future edition of IE Connections.
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Guam Opens Pacific-based Radon Training Center
Douglas Kladder
Director
Center for Environmental Research & Technology Inc.
Colorado Springs, Colo.Just in time for January’s Radon
Action Month, Guam Community College opened its doors as an
educational center for training radon measurement and mitigation
professionals addressing radon concerns associated with the unique
conditions found on a tropical island such as Guam. This will
significantly benefit not only individuals residing on Guam but also
contractors and engineers wanting to provide services to other
Pacific Rim locations and Asia.
But, wait a minute, why can’t a person just take the tried and
true mainland U.S. courses and apply it to other regions?
Unique Conditions Outside the Mainland United States
What is unique about the program being developed for Guam is that it
will focus on how to measure and to mitigate structures that are
commonly found throughout the Pacific Rim and Asia. In other words,
the common U.S. curriculum deals with wood-frame homes built over
basements in regions where winter means cold weather. In Guam, one
would be hard-pressed to find a basement, and structures there, like
many throughout Asia, are typically slab-on-grade and constructed of
steel-reinforced concrete to withstand earthquakes. I would also
venture to say that a snowflake has never made it to the island of
Guam unless it was shipped there under refrigeration – but they sure
have typhoons with winds that have been recorded over 200 miles per
hour.
Radon entry patterns in Guam and other Pacific islands such as
Okinawa are also different. The porous nature of coral-based islands
allows for significant soil gas entry as a function of external
influences such as rain or wind rather than thermal stack effect,
which is typically the driving force for mainland U.S. locations.
This causes radon spikes to be very dramatic and short-lived, which
can cause significant error when relying upon short-term
measurements. On Guam and other Pacific islands, one typically looks
at rainy season versus dry season rather than summer versus winter.
But on the other hand, the term “dry season” is a relative term
because a rainstorm in the “dry season” can consist of several
inches of rain, which can cause significant short-term spikes in
radon concentrations that can dramatically impact a short-term
reading. This is why Guam’s Environmental Protection Agency is
recommending long-term testing over short-term testing for its new
program.
The tightness of buildings and prevalence of air-conditioning
constitute another difference. Although Guam is a beautiful island
where opportunities for lying on a sandy beach with a cool one in
hand, it is also very warm and humid, and essentially every home and
office building has air-conditioning that operates 365 days out of
the year. Couple this fact with the needs to retain conditioned air
and to keep out driving rains during heavy storms and even super
typhoons, buildings are constructed extremely tight. In fact, like
much of Asia where wood is scarce, the buildings are made out of
concrete.
When a building has a very tight shell, the slightest amount of
mechanically induced vacuum, such as from exhaust fans as well
unbalanced HVAC systems, can create a huge interior negative
pressures that can cause radon to come flying in. This can lead to
significantly variable interior radon conditions that can change as
a function of occupant behavior or when portions of the
air-conditioning systems deteriorate.
Also, like many buildings in the Pacific and Asia, Guam’s are
built to withstand some pretty hefty earthquakes. After experiencing
an earthquake in Guam registering 8.2 on the Richter scale, I
personally was quite appreciative of their building practices.
However, they do make it challenging from a mitigation standpoint.
First, there is so much reinforcing steel that any core made through
a foundation wall or a floor is bound to impact re-bar, and, with
the salt conditions present on an island, the steel has to be
protected. The grade beams are also frequent and deep and the slab
area impacted by active soil depressurization system can be limited,
often causing the need for multiple suction points.
The earthquake-resistant construction also extends to roofs that
are typically made of concrete and have special membranes to ward
off the 80 to 100 inches of rainfall each year. In other words,
running a mitigation system up through the roof is not a good idea,
and in many cases without attic spaces, it is impossible to locate
the fan outside the envelope unless it is outside the home. Of
course, with wind speeds over 200 mph during typhoons, this means
exterior mounted fans have to be well secured and resistant to
flying coconuts.
Guam EPA, Community College Approach
As the previous dissertation indicated, there are some significant
differences between Guam and the mainland United States.
Furthermore, the application of mainland protocols and training
curriculum without adaptation is inappropriate and, as demonstrated
in previous attempts, downright confusing for students. The Guam EPA
and Guam Community College believe a national curriculum and
certification exam dealing with winter weather, basements and
crawlspaces would be irrelevant to study in Guam and make students
unprepared to deal with the realities of a tropical island. On the
flip side, it is unfair to citizens of Guam who may hire a
nationally trained and certified contractor and expect them to
competently address their needs. So, in the future, if you are a
nationally certified measurement of mitigation professional, be
prepared to learn some new things before performing work on Guam.
Although there have been previous attempts to have radon training
programs on Guam, they have not been sustainable because they relied
upon mainland trainers coming there. Guam Community College and Guam
EPA are taking a different approach in that they are training local
contractors to be instructors. The community college has identified
some core trainers who have experience either in radon or building
sciences in Guam.
In addition to becoming nationally certified, the trainers
additionally participate in finalizing the Guam-specific curriculum
and the details of the island’s proficiency program. In this manner,
they will have a greater understanding of the differences between
U.S. and Guam programs. Furthermore, they will form a core group
that can assemble future data and experiences and incorporate it
into the experiential base of the curriculum for future offerings.
What is also unique about the program is that the majority of the
curriculum will be recorded audio and video that future students can
access at their convenience rather than having to wait for a formal
class. Guam Community College will periodically host classroom
sessions and mitigation demonstration projects, with the core
trainers facilitating classroom sessions and mentoring new students.
With the combination of distance learning approaches that provide a
consistent program and allow for the inclusion of off-island
experts, coupled with local technical support and classroom
sessions, it is felt that Guam Community College will have a solid
and sustainable program. In fact, the proposed approach was solid
enough to obtain funding from Region 9 EPA through Guam EPA.
It will be interesting to observe how this approach works. If
successful, it will not only provide a tremendous resource for other
nations in the Pacific Rim that are facing radon issues but will
also provide a model that could work very well within the mainland
U.S. as well. Hats off to Guam EPA and Guam Community College!
As always, who says there is nothing new in radon?
Douglas Kladder is director of the Center for Environmental
Research and Technology Inc. He can be reached by e-mail at
dougkladdr@aol.com or by
phone at (719) 477-1714.
Editor’s note: The Center for Environmental Research & Technology
Inc. devised the course discussed in this column and coordinated
with Guam EPA and Guam Community College to begin providing the
course in January. |
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H. Quantifying Bacteria Levels in Water
Categories 1–3
Dr. Bob Brandys
President
Occupational and Environmental Health Consulting Services Inc.
Hinsdale, Ill.
In any water intrusion situation, typically, one of the most
important questions to answer is: What was the quality of the
intruding water? The IICRC S500 “Standard and Reference Guide for
Professional Water Damage Restoration” contains qualitative,
descriptive definitions of intruding water, dividing the substance
into three categories.The descriptive nature of definitions of
Categories 1, 2 and 3 offers a handy guide for remediators who need
to make expedient judgment calls on water quality and remediation
protocols. The qualitative nature of these definitions may be
adequate for smaller remediation jobs where the cost of bacteria
testing could exceed the remediation and relocation costs or when
the length of time necessary to analyze bacteria samples is not
acceptable to the parties involved.
However, in some larger water intrusion incidents, the quality of
the water involved and the subsequent required level of remediation
may be in question and significantly impact the cost of remediation.
In such cases, a more definitive and quantitative characterization
of water quality and its residual contamination could be useful. At
this point in time, S500 provides no guidance on what specific
microbial or chemicals levels are present in these water categories.
A recent large loss occurred in the Chicago area where the issue
of the water category was a very significant question. The water
intrusion occurred during a storm-related, four-hour power outage in
a very large apartment complex. All of the ground-level apartments
were flooded with a few inches of water. Once the power returned,
the sump pumps removed the majority of the water from the buildings.
A drying crew responded within 12 hours to dry the affected areas
completely in less than 24 hours.
During the flooding, most people reported that the water came
from the sump pump in the laundry rooms in the buildings. The gutter
downspouts from the roof were directly connected to the sump pump
pits in the laundry room. When the power outage occurred, the roof
water flooded the buildings.
However, the property owners claimed some people reported that it
was a sewage backflow. This complex was below grade and had its own
main ejector station. It was not directly connected to the local
sewer main. Hence, there was no backflow from the sewer main. In
addition, since this power outage occurred in the middle of the
night, the amount of sewage generated by occupants at that time
would have been minimal. Therefore, it was unlikely that sewage
backflow was a major source of the intruding water.
The property owners rejected the argument that the roof water was
the main water source and insisted that even a small amount of
sewage made this a black water incident. They wanted everything in
the 50 affected apartments replaced, even the major appliances.
Actually, S500 provides conflicting interpretations in this
particular case. According to S500, if the incident was
sewage-related, then this would be a Category 3 water situation.
However, most of the water was rainwater from the roof that flowed
into a sump pit. Since foundation perimeter drainage water is
“seepage due to hydrostatic pressure,” S500 says this is Category 2
water. Was this situation seepage, or could this water be considered
falling rainwater – Category 1? S500 has no specific categorization
for roof run-off. Did all of the furnishings need to be disposed of
or not? The insurance company decided to retain an environmental
consultant to resolve the water quality question.
In classifying the category of water in this situation, it was
assumed that the major concern was microbial contamination and no
other sources of contamination were involved. This was an apartment
complex, not an industrial site, so there should be no significant
chemical contamination questions. Based on this assumption, it was
decided to use the quantitative microbial levels in the research
literature and bacterial water quality regulations to develop
appropriate bacterial level classifications for S500 Category 1, 2
and 3 water. These numbers could then be used categorize the quality
of water involved in this incident.
Before we review the various bacterial water quality standards,
we should review some of the typical bacterial test methods that are
used to determine water quality. These are:
- Heterotrophic plate count, or HPC, also known as total plate
count: This is the most common test method used to analyze
water. It estimates the total amount of bacteria in the water.
- Coliform bacteria: This test was initially developed to look
for cross-contamination between the water in a sewerage system
and well water. It looks for bacteria that live in the lower
intestines of warm-blooded animals (including birds and mammals)
that are necessary for the proper digestion of food. The
assumption was that if these bacteria are found in potable
water, then there must be a connection between sewer water and
potable water. However, coliform bacteria can also be found in
soil and natural waters, so a sewerage system is not always the
source.
- Escheria coli (E. coli) Bacteria: This is a test for a
specific coliform bacteria known as E. coli. Some strains, such
as O157, are infective and can cause serious disease. Initially,
it was thought that E. coli came only from human waste. Today,
we know that there are many other sources that can contaminate
both food and water. Table 1 shows some examples of typical
levels of E. coli from humans and other species. (What this
table indicates is that in evaluating potential bacterial
contamination in dwellings, the existence of pets can radically
skew background or preexisting measurements of E. coli in an
environment.)
| Table 1: Viable E. coli bacteria levels
for common animals feces |
| Human |
5,000,000 cfu/gram |
| Cat |
40,000,000 cfu/gram |
| Dog |
32,000,000 cfu/gram |
| Goose |
310,000 cfu/gram |
- Fecal coliform: This is another test for a specific coliform
bacteria known as fecal coliform. As the term implies, these are
coliform bacteria that are directly related to fecal
contamination.
- Fecal streptococci: These bacteria are members of the
Enterococcus and Streptococcus groupings of bacteria. They are
characterized as being round in shape and, again, fecal in
origin.
Now that we have covered the basic definitions of the standard
bacteriological water quality tests, we can review the relevant
regulatory water quality standards and research literature to see
how this information can be used to quantify the three categories of
intruding water.
Category 1 Water Standards
S500 defines Category 1 water as originating from a sanitary water
source that does not pose a substantial risk from dermal, ingestion,
or inhalation exposure. Some examples are broken water supply, tub
or sink overflows with no contaminants, melting ice or snow, falling
rainwater, broken toilet tank, and broken toilet bowls with no
contaminants or additives.
The first place to start identifying bacterial standards for
Category 1 water are microbial standards for potable water or water
that originates from a sanitary source. The most common source of
sanitary water is potable or drinking water. Table 2 shows the
applicable HPC bacterial limits for potable drinking water. The
consensus is that potable water should contain less than 50,000
colony-forming units per 100 milliliters.
| Table 2: Applicable standards for
potable water interpretation (a.k.a. Category 1) |
| Standard-setting body or law |
Maximum level for HPC |
| U.S. Environmental Protection Agency
Drinking Water Safety Act* |
<50,000
cfu/100 ml |
| Brazil (potable drinking water) |
<50,000
cfu/100 ml |
| Hong Kong Food and Hygiene Department
|
<50,000
cfu/100 ml |
| Pharmaceutical/medical device industry
(acceptable incoming potable water) |
<50,000
cfu/100 ml |
| American Water Works Association ANSI
Standard C651.92 |
<50,000
cfu/100 ml |
* Although the Drinking Water Safety Act is not a legal
U.S. standard per se, the EPA recognizes that properly chlorinated
and maintained potable water systems will have less than 500 cfu/ml.
The EPA also states, “An informal standard of 500 [cfu/ml] of
potable water has been used as an indicator of the integrity of
distribution systems.”
The second criterion listed in S500 for Category 1 water is that
it “does not pose substantial risk from dermal, ingestion, or
inhalation exposure” (emphasis added). Clearly, water from a
properly maintained swimming pool does not pose a substantial risk
from these types of exposure; so, swimming pool standards should be
applicable to Category 1 water as well. Tables 3, 4 and 5 show
various regulatory standards for HPC, E. coli and coliform
standards, respectively, for swimming pool water.
| Table 3: Heterotrophic
plate count standards for swimming pools |
| Agency
|
Maximum
level (in cfu/100 ml) |
| U.S. Army |
< 20,000 |
| Massachusetts
|
< 20,000 |
| Arizona < 20,000 |
< 20,000 |
| Australia |
< 10,000 |
| Note: The
standard for HPC in drinking water is higher than for
swimming pools. |
|
| Table 4:
Thermotolerant coliform plate count standards for
swimming pools |
| Agency
|
Maximum
level (in cfu/100 ml) |
United National
Environment
Programme/World Health |
< 100 (50%
average) |
| Organization (1985)
interim criteria for recreational waters |
< 1,000 max. (1 in 10 samples) |
| Maine |
< 2 |
| Arizona |
< 2 |
|
| Table 5: E. coli
standards for swimming pools |
| Agency
|
Maximum
level (in cfu/100 ml) |
| New Hampshire |
≤ 88 |
Another useful “minimal” risk example is the Texas Natural Resource
Conservation Commission, which has bacterial standards for Type I
reclaimed water. Type I reclaimed water “can be applied on crops
when workers are present.” This means that Type I reclaimed water
also does not pose a substantial risk from dermal, ingestion, or
inhalation exposure; so, these standards would also apply to
Category 1 water.
Other uses of Type I reclaimed water include reservoir tanks for
toilet bowls and urinals. These uses are examples of Category 1
water is the S500 definition. Table 6 shows the fecal coliform
bacterial standards for Type I reclaimed water.
| Table 6: Fecal
coliform standards for Type I reclaimed water |
| Type I reclaimed water |
Maximum
level (in cfu/100 ml) |
| Fecal coliform (average)
|
< 20 |
| Fecal coliform (not to
exceed) |
< 75 |
| Source: Texas
Natural Resource Conservation Commission |
In summary, based on the regulatory standards in Tables 2–5,
Category 1 water should contain less than 50,000 cfu/100 ml HPC
bacteria, less than 100 cfu/100 ml coliform bacteria, less than 75
cfu/100 ml fecal coliform, and less than or equal to 88 /100 ml E.
coli.
Category 2 Water Standards
S500 defines Category 2 water as water that “contains significant
contamination and has the potential to cause discomfort or sickness
if contacted or consumed by humans.” Some examples include
discharges from dishwashers, discharges from washing machines,
overflows from washing machines, overflows from a toilet bowl that
contains urine, groundwater seepage due to hydrostatic pressure,
broken aquariums, and punctured waterbeds. Such water, S520 says,
“can contain potentially unsafe levels of microorganisms or
nutrients for microorganisms, as well as other organic or inorganic
matter.”
Some ambiguity exists in this definition with its use of the term
“contacted” in “if contacted or consumed by humans.” This would not
appear to include an inhalation risk. However, since inhalation risk
is already included in the Category 1 definition, it would seem to
imply that an inhalation risk could also be present for more
hazardous Category 2 water.
For some perspective on the “contact risk” concept, the Texas
Natural Resource Conservation Commission has bacterial limits for
Type II reclaimed water standards for irrigation. Type II water can
only be applied to crops when people are not present. This implies a
“contact risk” from this type of water. The bacterial limit
standards for Type II reclaimed water are shown in Table 7. These
standards clearly fall into the Category 2 water definition and
provide a “contact risk” bacterial limit between Category 1 and
Category 2 water.
| Table 7: Fecal
coliform and total coliform standards for Type II
reclaimed water |
| Type II reclaimed
water |
Maximum
level (in cfu/100 ml) |
| Fecal coliform
|
(average) <
200 * |
| Fecal coliform
|
(not to
exceed) < 800 * |
| Total coliform
|
< 2,000 ** |
* Texas
Natural Resource Conservation Commission
** Valentina Lazarova Akiçca Bahri, “Water Reuse for
Irrigation, Agriculture, Landscapes, and Turf Grass,”
CRC Press. |
Another example in the S500 Category 2 water definition is that
consumption of the water may cause sickness or discomfort. The World
Health Organization has established HPC standards for edible ice.
The concern here is when ice containing high levels of bacteria
melts in a beverage and makes people sick. Table 8 shows the WHO’s
HPC standards for edible ice for both healthy and immunocompromised
people.
| Table 8: Heterotrophic
plate counts for edible ice |
| Standard-setting body
or law |
Maximum
level (in cfu/100 ml) |
World Health Organization
standard for edible ice* |
< 5,000,000 |
World Health Organization
standard for edible ice for infants and elderly with
suppressedimmune systems ** |
< 300,000 |
* Geldreich,
E. E. et al., 1975
** Richardson, 1998 |
In summary, based on the regulatory standards in Tables 6
and 7, the bacterial limits between Category 1 and Category 2 water
appear to be well defined.
Category 3 Water
S500 defines Category 3 water as “grossly contaminated” with harmful
agents that may be pathogenic or toxigenic. Some examples of this
category include sewage, toilet overflows originating from beyond
the trap (regardless of visible content or color), all forms of
flooding from seawater, ground surface water, rising water from
rivers or streams, and wind-driven rain from hurricanes, tropical
storms or other rain events. (Water from rain events may contain
silt, organic matter, pesticides, heavy metals, regulated materials,
or toxic organic substances.)
In dealing with Category 3 water, the worst-case microbial
situation is sewage. Since there are no regulatory standards for
sewage bacterial levels, the reference literature was reviewed to
identify the typical levels of bacteria in sewage. Table 9 shows the
typical microbial level of sewage for total coliforms, fecal
coliforms and fecal streptococci found in various U.S. municipal
sewage systems.
| Table 9: Coliform and
streptococci levels in typical sewage |
| Sewer
source |
Total
coliforms |
Fecal
coliforms |
Fecal
streptococci |
| |
(in cfu/100 ml) |
(in cfu/100 ml) |
(in cfu/100 ml) |
| Esparto,
Calif. |
23,500,000 |
6,200,000 |
- |
| Shastina,
Calif. |
9,600,000 |
2,300,000 |
- |
| Los Banos,
Calif. |
62,000,000 |
23,000,000 |
- |
| Anaka, Minn. |
47,400,000 |
10,200,000 |
- |
| Newport,
Minn. |
13,600,000 |
3,580,000 |
- |
| Red Wing,
Minn. |
17,700,000 |
4,050,000 |
- |
| Mankato,
Minn. |
5,525,000 |
2,630,000 |
- |
| Oakwood
Beach, N.J. |
13,250,000 |
4,240,000 |
- |
| Perth Amboy,
N.J. |
1,600,000 |
387,000 |
- |
| Middlesex,
N.J. |
12,900,000 |
1,070,000 |
- |
| Keyport,
N.J. |
2,210,000 |
641,000 |
- |
| Omaha, Neb. |
45,800,000 |
5,360,000 |
- |
| Anderson,
Ohio |
17,200,000 |
4,600,000 |
- |
| Cincinnati,
Ohio |
34,800,000 |
4,900,000 |
- |
| Moorhead,
Minn. |
- |
1,600,000 |
- |
| Linwood,
Ohio |
- |
10,900,000 |
2,470,000 |
| Preston,
Idaho |
- |
340,000 |
64,000 |
| Fargo, N.D. |
- |
1,300,000 |
290,000 |
| Lawrence,
Mass. |
- |
17,900,000 |
4,500,000 |
| Monroe,
Mich. |
- |
19,200,000 |
700,000 |
| Denver,
Colo. |
- |
49,000,000 |
2,900,000 |
| Minimum
value |
1,600,000 |
340,000 |
64,000 |
| Median
value |
15,400,000 |
4,240,000 |
1,585,000 |
|
Source: Edwin E. Geldreich, “Microbial Quality of Water
Distribution Systems,” 1992. |
As one can see in Table 9, the range of total coliforms for
typical sewage water varies from 1.6 million to 62 million cfu/100
ml. Comparing the range of fecal coliform bacteria in sewage to the
level in Type I reclaimed water (Table 6), shows that the fecal
coliform levels in sewage are approximately 2,000 to 200,000 times
higher than Type I reclaimed water. Similar differences exist for
the other types of bacteria. Therefore, if we take the lowest
bacteria levels found in this research literature of sewage, these
level lowest levels should be a conservative minimum bacterial
classification range for Category 3 sewage water.
In summary, based on the research literature, Category 3 water
would contain greater than 1.6 million cfu/100 ml of total coliform
and greater than or equal to 340,000 cfu/100 ml fecal coliform.
Application of Category 1, 2, and 3 Bacterial Water Quality
Guidelines
Table 10 summarizes the total plate count, total coliform and fecal
coliform bacterial limits for water that meet the definitions in
S500 of Category 1, 2 and 3 water. Water being tested should comply
with all three of the standards to meet a specific category
definition. Here is how to do it.
| Table 10: Summary of
suggested Category 1, 2 and 3 bacterial ranges in water |
| Water
category |
Total
plate count |
Total
coliform |
Fecal
coliform |
| |
(in cfu/100 ml) |
(in cfu/100 ml) |
(in cfu/100 ml) |
| Category 1 |
< 50,000 |
< 100 |
≤ 75 * |
| Category 2 |
≥ 50,000 and <50,000,000 |
≥ 100 and <1,600,000 |
≥ 75 * and < 340,000 |
| Category 3 |
≥50,000,000 and TNTC** |
≥1,600,000 |
≥340,000 |
* Uncontaminated recycled water used in toilets and
urinals
** TNTC = too numerous to count. This varies depending
upon the serial dilutions employed by the lab but
typically is 50,000,000 cfu/100 ml. |
At the start of your water removal process, take at least three
pint-size samples of the intruding water. The samples should be
taken using sterile water sample bottles. These bottles are
available at very low cost from water analysis laboratories. After
taking the water samples, keep the samples in a cooler with an ice
pack and ship them to the laboratory within 24 hours. Have the
laboratory analyze each sample for total plate count, total coliform
and fecal coliform. The analysis will usually take five to seven
days. By this time, the building should be dried.
Compare the laboratory analysis results to the numbers in Table
10. If the results show bacteria levels in the Category 1 range,
then very little cleaning and disinfection will be needed. On the
other hand, if the numbers are close to Category 3 levels,
significant cleaning and disinfection will be needed to reduce
bacteria levels to normal ranges.
Bob Brandys has served as president of his own environmental
consulting firm since 1984 and has authored or coauthored three
books and numerous publications on chemical safety and microbial
control for the hospital and healthcare manufacturing sector as well
as the mold consulting and remediation industries. He can be reached
by e-mail at
bobb@safety-epa.com or by phone at (630) 325-2083. |
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